EP3881932A1 - Porous ceramic body to reduce emissions - Google Patents

Porous ceramic body to reduce emissions Download PDF

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Publication number
EP3881932A1
EP3881932A1 EP21170501.7A EP21170501A EP3881932A1 EP 3881932 A1 EP3881932 A1 EP 3881932A1 EP 21170501 A EP21170501 A EP 21170501A EP 3881932 A1 EP3881932 A1 EP 3881932A1
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EP
European Patent Office
Prior art keywords
walls
porous ceramic
zeolite
substrate
honeycomb body
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
EP21170501.7A
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German (de)
English (en)
French (fr)
Inventor
Mallanagouda Dyamanagouda Patil
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Corning Inc
Original Assignee
Corning Inc
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Filing date
Publication date
Application filed by Corning Inc filed Critical Corning Inc
Publication of EP3881932A1 publication Critical patent/EP3881932A1/en
Pending legal-status Critical Current

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    • B01J37/00—Processes, in general, for preparing catalysts; Processes, in general, for activation of catalysts
    • B01J37/02—Impregnation, coating or precipitation
    • B01J37/024—Multiple impregnation or coating
    • B01J37/0244—Coatings comprising several layers
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01D—SEPARATION
    • B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34—Chemical or biological purification of waste gases
    • B01D53/92—Chemical or biological purification of waste gases of engine exhaust gases
    • B01D53/94—Chemical or biological purification of waste gases of engine exhaust gases by catalytic processes
    • B01D53/9445—Simultaneously removing carbon monoxide, hydrocarbons or nitrogen oxides making use of three-way catalysts [TWC] or four-way-catalysts [FWC]
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    • B01D—SEPARATION
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    • B01D53/34—Chemical or biological purification of waste gases
    • B01D53/92—Chemical or biological purification of waste gases of engine exhaust gases
    • B01D53/94—Chemical or biological purification of waste gases of engine exhaust gases by catalytic processes
    • B01D53/9459—Removing one or more of nitrogen oxides, carbon monoxide, or hydrocarbons by multiple successive catalytic functions; systems with more than one different function, e.g. zone coated catalysts
    • B01D53/9477—Removing one or more of nitrogen oxides, carbon monoxide, or hydrocarbons by multiple successive catalytic functions; systems with more than one different function, e.g. zone coated catalysts with catalysts positioned on separate bricks, e.g. exhaust systems
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    • B01D53/94—Chemical or biological purification of waste gases of engine exhaust gases by catalytic processes
    • B01D53/9481—Catalyst preceded by an adsorption device without catalytic function for temporary storage of contaminants, e.g. during cold start
    • B01D53/9486—Catalyst preceded by an adsorption device without catalytic function for temporary storage of contaminants, e.g. during cold start for storing hydrocarbons
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    • C04—CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04B—LIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B2235/00—Aspects relating to ceramic starting mixtures or sintered ceramic products
    • C04B2235/02—Composition of constituents of the starting material or of secondary phases of the final product
    • C04B2235/30—Constituents and secondary phases not being of a fibrous nature
    • C04B2235/32—Metal oxides, mixed metal oxides, or oxide-forming salts thereof, e.g. carbonates, nitrates, (oxy)hydroxides, chlorides
    • C04B2235/3205—Alkaline earth oxides or oxide forming salts thereof, e.g. beryllium oxide
    • C—CHEMISTRY; METALLURGY
    • C04—CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04B—LIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B2235/00—Aspects relating to ceramic starting mixtures or sintered ceramic products
    • C04B2235/02—Composition of constituents of the starting material or of secondary phases of the final product
    • C04B2235/30—Constituents and secondary phases not being of a fibrous nature
    • C04B2235/32—Metal oxides, mixed metal oxides, or oxide-forming salts thereof, e.g. carbonates, nitrates, (oxy)hydroxides, chlorides
    • C04B2235/3217—Aluminum oxide or oxide forming salts thereof, e.g. bauxite, alpha-alumina
    • F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F01—MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
    • F01N—GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR MACHINES OR ENGINES IN GENERAL; GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR INTERNAL COMBUSTION ENGINES
    • F01N2330/00—Structure of catalyst support or particle filter
    • F01N2330/06—Ceramic, e.g. monoliths
    • F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F01—MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
    • F01N—GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR MACHINES OR ENGINES IN GENERAL; GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR INTERNAL COMBUSTION ENGINES
    • F01N2370/00—Selection of materials for exhaust purification
    • F01N2370/02—Selection of materials for exhaust purification used in catalytic reactors
    • F01N2370/04—Zeolitic material
    • F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F01—MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
    • F01N—GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR MACHINES OR ENGINES IN GENERAL; GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR INTERNAL COMBUSTION ENGINES
    • F01N2510/00—Surface coverings
    • F01N2510/06—Surface coverings for exhaust purification, e.g. catalytic reaction
    • F01N2510/063—Surface coverings for exhaust purification, e.g. catalytic reaction zeolites
    • F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F01—MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
    • F01N—GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR MACHINES OR ENGINES IN GENERAL; GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR INTERNAL COMBUSTION ENGINES
    • F01N3/00—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust
    • F01N3/08—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous
    • F01N3/0807—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous by using absorbents or adsorbents
    • Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02T—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO TRANSPORTATION
    • Y02T10/00—Road transport of goods or passengers
    • Y02T10/10—Internal combustion engine [ICE] based vehicles
    • Y02T10/12—Improving ICE efficiencies

Definitions

  • Exemplary embodiments of the present disclosure relate to porous ceramic bodies to reduce emissions, in particular porous ceramic bodies having zeolite adsorber in wall and three-way catalyst (TWC) on wall to reduce hydrocarbons and volatile organic components (HC/VOC) emissions, an exhaust gas system incorporating the same, and methods of manufacturing the same.
  • porous ceramic bodies to reduce emissions, in particular porous ceramic bodies having zeolite adsorber in wall and three-way catalyst (TWC) on wall to reduce hydrocarbons and volatile organic components (HC/VOC) emissions, an exhaust gas system incorporating the same, and methods of manufacturing the same.
  • TWC three-way catalyst
  • After-treatment of exhaust gas from internal combustion engines may use catalysts supported on high-surface area substrates and, in the case of diesel engines and some gasoline direct injection engines, a catalyzed or non-catalyzed filter for the removal of carbon soot particles.
  • Porous ceramic flow-through honeycomb substrates and wall-flow honeycomb filters may be used in these applications.
  • Exemplary embodiments of the present disclosure provide a porous ceramic body having zeolite disposed inside pores of walls of the porous ceramic body and three-way catalyst (TWC) disposed on wall surfaces of the porous ceramic body.
  • TWC three-way catalyst
  • Exemplary embodiments of the present disclosure also provide a method of manufacturing a porous ceramic body having zeolite disposed inside pores of walls of the porous ceramic body and three-way catalyst (TWC) disposed on the wall surfaces of the porous ceramic body.
  • TWC three-way catalyst
  • Exemplary embodiments of the present disclosure also provide an exhaust gas system including the porous ceramic body having zeolite disposed inside pores thereof and TWC disposed on wall surfaces thereof.
  • An exemplary embodiment discloses a porous ceramic body comprising a substrate of porous walls forming channels extending from a first end face to a second end face.
  • the porous ceramic honeycomb body comprises an in wall zeolite catalyst disposed inside pores of a first portion of the walls, and a three way catalyst (TWC) disposed on wall surfaces of the first portion of the walls.
  • TWC three way catalyst
  • An exemplary embodiment also discloses a porous ceramic body comprising a substrate of porous walls forming channels extending from a first end face to a second end face.
  • the porous ceramic honeycomb body comprises a three way catalyst (TWC) disposed on wall surfaces of at least a portion of the walls, wherein the substrate comprises an extruded zeolite catalyst.
  • TWC three way catalyst
  • An exemplary embodiment also discloses a method of manufacturing a ceramic article.
  • the method comprises extruding a zeolite catalyst porous ceramic body and disposing three way catalyst (TWC) on wall surfaces of the walls of the porous ceramic body.
  • TWC three way catalyst
  • An exemplary embodiment also discloses a method of manufacturing a ceramic article.
  • the method comprises disposing zeolite catalyst inside pores in walls of a first portion of walls of a porous ceramic body; and disposing three way catalyst (TWC) on wall surfaces of at least a portion of the first portion of the walls of the porous ceramic body.
  • TWC three way catalyst
  • An exemplary embodiment also discloses an exhaust gas system.
  • the exhaust gas system includes a housing having an inlet configured to accept an exhaust gas stream to be purified, the housing having a chamber configured to flow the exhaust gas stream through a porous ceramic honeycomb body to purify the exhaust gas stream, and the housing having an outlet configured to emit the purified exhaust gas stream.
  • the porous ceramic honeycomb body disposed in the housing comprises a substrate of porous walls forming channels extending from a first end face to a second end face.
  • the porous ceramic honeycomb body comprises an in wall zeolite catalyst disposed inside pores of walls of a first portion of the walls and a three way catalyst (TWC) disposed on wall surfaces of at least a portion of the walls of the first portion of walls.
  • TWC three way catalyst
  • the disclosed article, and the disclosed method of making the article provide one or more advantageous features or aspects, including for example as discussed below.
  • Features or aspects recited in any of the claims are generally applicable to all facets of the disclosure. Any recited single or multiple feature or aspect in any one claim can be combined or permuted with any other recited feature or aspect in any other claim or claims.
  • top, bottom, side, upper, lower, vertical, and horizontal are used, the disclosure is not so limited to these exemplary embodiments. Instead, spatially relative terms, such as “top”, “bottom”, “horizontal”, “vertical”, “side”, “beneath”, “below”, “lower”, “above”, “upper” and the like, may be used herein for ease of description to describe one element or feature's relationship to another element(s) or feature(s) as illustrated in the figures. It will be understood that the spatially relative terms are intended to encompass different orientations of the device in use or operation in addition to the orientation depicted in the figures.
  • the exemplary term “below” can encompass both an orientation of above and below.
  • the device may be otherwise oriented (rotated 90 degrees or at other orientations) and the spatially relative descriptors used herein interpreted accordingly.
  • the term “about” also encompasses amounts that differ due to aging of a composition or formulation with a particular initial concentration or mixture, and amounts that differ due to mixing or processing a composition or formulation with a particular initial concentration or mixture.
  • indefinite article “a” or “an” and its corresponding definite article “the” as used herein means at least one, or one or more, unless specified otherwise.
  • an active material is disposed inside the pores of a substrate and a three-way catalyst (TWC) is disposed on the surfaces of the channel walls of the substrate as will be described in more detail below.
  • TWC three-way catalyst
  • zeolite is disposed in the pores directly on the pore surfaces and the TWC is disposed directly on the wall surfaces.
  • An active material as used herein refers to material which can modify a gaseous mixture, by reaction with the mixture components, by catalytic activity, or by sorbing activity, or desorbing activity.
  • the active material is preferably sorbing material and/or catalytic material.
  • the sorbing material or sorbing agents take up and hold substances by either absorption or adsorption.
  • a sorbing agent is present in the substrate pores to take up or remove selected constituents from a gaseous mixture under certain conditions. These constituents can then desorb under certain conditions which are predetermined.
  • the term "sorbing material" or "sorbing agent” as used in the present disclosure can refer to one or a plurality of sorbing agents.
  • Adsorption is the taking up of molecules by physical or chemical forces, termed respectively, physical or chemical adsorption.
  • the term "adsorbing agent" according to the present disclosure refers to at least one adsorbing agent. There can be more than one type of adsorbing agent in the pores of the substrate wall. The specific adsorbers can vary depending on the application.
  • Catalyst material according to the present disclosure refers to a catalyst metal or catalyst metal oxide on a support. Catalyst material includes also molecular sieves, such as zeolites when used in conversions such as, e.g., in cracking of hydrocarbons or oxidation, etc.
  • Example adsorbing agents that are suited for removal of hydrocarbons are those that adsorb at relatively low temperatures and desorb at relatively high temperatures.
  • adsorbing agents that adsorb hydrocarbons at engine start-up temperatures which are typically less than about 150 °C, and desorb at engine operating temperatures which are typically greater than about 150 °C can be used.
  • examples of adsorbing agents which can be used as described herein without limitation are molecular sieves, activated carbon, transition aluminas, activated silicas, and combinations of these.
  • Molecular sieves are crystalline substances having pores of size suitable for adsorbing molecules.
  • Some example types of molecular sieves without limitation are carbon molecular sieves, zeolites, aluminophosphates, metallophosphates, silicoaluminophosphates, and combinations of these.
  • Carbon molecular sieves have well defined micropores made out of carbon material.
  • the active material can be without limitation, a metal exchanged or impregnated zeolite, for example, ZSM-5, beta-zeolites, mordenite, Y-zeolites, ultrastabilized Y-zeolites, aluminum phosphate zeolites, gmelinite, mazzite, offretite, ZSM-12, ZSM-18, Berryllophosphate-H, boggsite, SAPO-40, SAPO-41, combinations thereof, and mixtures thereof.
  • a metal exchanged or impregnated zeolite for example, ZSM-5, beta-zeolites, mordenite, Y-zeolites, ultrastabilized Y-zeolites, aluminum phosphate zeolites, gmelinite, mazzite, offretite, ZSM-12, ZSM-18, Berryllophosphate-H, boggsite, SAPO-40, SAPO-41, combinations thereof, and mixtures thereof.
  • the active material will be referred to herein as a zeolite for convenience in the further detailed description.
  • Zeolite, zeolite adsorber, zeolite catalyst, zeolite-based catalyst, and the like are used herein interchangeably for convenience according to these exemplary embodiments of the disclosure.
  • the TWC can include noble metal oxidation catalysts such as Pt, Rh, and/or Pd with a support such as alumina, ceria, titania, lanthana, zirconia etc.
  • the oxidation catalyst serves to oxidize the hydrocarbons mainly, to innocuous products as carbon dioxide and water, which are suitable for passing into the atmosphere.
  • the TWC can include a catalyst for conversion of NO x , CO, and hydrocarbons to innocuous products.
  • the TWC can include noble metal as e.g., Pt, Pd, Rh, or combinations thereof on alumina, ceria, lanthana, zirconia, yttria, or combinations thereof.
  • the TWC suited to the practice of exemplary embodiments of the present disclosure for stationary power plant exhaust conversion can include SCR catalyst for NOx reduction such as zeolite-based catalysts having transition metal or metals ion exchanged.
  • SCR catalyst for NOx reduction such as zeolite-based catalysts having transition metal or metals ion exchanged.
  • Some example catalysts are Fe mordenite, Cu mordenite, ZSM-5 H + form, and V 2 O 5 /TiO 2 .
  • the TWC suited to the practice of exemplary embodiments of the present disclosure for auto exhaust conversion are, for example, Pt on ceria-alumina combined with Rh on zirconia.
  • the Pt-ceria-alumina and the Rh-zirconia can be combined and applied at once, as in a single coating or they can be applied in separate coatings.
  • Another suitable catalyst is Pt/Pd/Rh on gamma alumina with a rare earth oxide such as ceria.
  • HC hydrocarbons and volatile organic components
  • FIG. 1A shows a honeycomb body 100 including a plurality of intersecting walls 110 that form mutually adjoining cell channels 112 extending axially in direction "A" between opposing end faces 114, 116.
  • FIG. 1B shows a schematic cross section through the honeycomb body 100 of FIG. 1A.
  • FIG. 1C shows a schematic top view of the honeycomb body 100 of FIG. 1A .
  • Cell is generally used herein when referring to intersecting walls in cross section of the honeycomb body and "channel” is generally used when referring to a cell extending between the end faces 114, 116. Cell and channel may be used interchangeably as well as "cell channel”.
  • the top face 114 refers to the first end face and the bottom face 116 refers to the second end face of the honeycomb body 100 positioned in FIG. 1A , otherwise the end faces are not limited by the orientation of the honeycomb body 100.
  • the top face 114 may be an inlet face and the bottom face 116 may be an outlet face of the honeycomb body 100 or the top face 114 may be an outlet face and the bottom face 116 may be an inlet face of the honeycomb body 100.
  • Cell density can be between about 100 and 900 cells per square inch (cpsi).
  • Typical cell wall thicknesses can range from about 0.025 mm to about 1.5 mm (about 1 to 60 mil).
  • honeycomb body 100 geometries may be 400 cpsi with a wall thickness of about 8 mil (400/8) or with a wall thickness of about 6 mil (400/6).
  • Other geometries include, for example, 100/17, 200/12, 200/19, 270/19, 300/4, 600/4, 400/4, 600/3, and 900/2.
  • honeycomb body 100 is intended to include a generally honeycomb structure but is not strictly limited to a square structure.
  • hexagonal, octagonal, triangular, rectangular or any other suitable cell shape may be used.
  • the cross section of the depicted cellular honeycomb body 100 is circular, it is not so limited, for example, the cross section can be elliptical, square, rectangular, other polygonal shape, or other desired shape, and a combination thereof.
  • porous ceramic body can refer to a honeycomb body, but is not so limited and can also refer to trough filters, radial flow filters, and the like. Ceramic body compositions are not particularly limited and can comprise major and minor amounts of cordierite, aluminum-titanate, mullite, ⁇ -spodumene, silicon carbide, zeolite and the like, and combinations thereof. As a further example, the ceramic honeycomb body can comprise an extruded zeolite or other extruded catalyst.
  • porous ceramic honeycomb bodies may be accomplished by the process of plasticizing ceramic powder batch mixtures, extruding the mixtures through honeycomb extrusion dies to form honeycomb extrudate, and cutting, drying, and firing the extrudate to produce ceramic honeycomb bodies of high strength and thermal durability having channels extending axially from a first end face to a second end face.
  • a ceramic honeycomb body includes ceramic honeycomb monoliths and ceramic segmented honeycomb bodies.
  • a co-extruded or an after-applied exterior skin may form an outer peripheral surface extending axially from a first end face to a second end face of the ceramic honeycomb bodies.
  • Each channel of the honeycomb bodies defined by intersecting walls (webs), whether monolithic or segmented, can be plugged at an inlet face or an outlet face to produce a filter. When some channels are left unplugged a partial filter can be produced.
  • the honeycomb body, whether monolithic or segmented, can be catalyzed to produce a substrate.
  • a non-plugged honeycomb body is generally referred to herein as a substrate.
  • the catalyzed substrate can have an after applied catalyst or comprise an extruded catalyst.
  • filters and partial filters can be catalyzed to provide multi-functionality.
  • the ceramic honeycomb bodies thus produced are widely used as catalyst supports, membrane supports, as wall-flow filters, as partial filters, and the like or as combinations thereof for cleaning fluids such as purifying engine exhausts.
  • FIG. 2 illustrates the engine out cold start HC emissions in ppm carbon 202 (dashed line) and the engine out exhaust temperature 204 (solid line) over time in seconds during an Environmental Protection Agency (EPA) Federal Test Procedure-75 (FTP-75) cycle for a 3.8L V6 engine in a vehicle.
  • EPA Environmental Protection Agency
  • FTP-75 Federal Test Procedure-75
  • the density can be about 30% less than conventional porous ceramic honeycomb substrates having similar cell density and wall thickness.
  • a 400/6 conventional porous ceramic honeycomb substrate of cordierite can have a density of about 0.41 g/cm 3 with about 27 percent porosity (%P), whereas the 400/6 low mass porous ceramic honeycomb substrate of cordierite can have a density of about 0.31 g/cm 3 with about 45 %P, a density of about 0.25 g/cm 3 with about 55 %P, or a density of about 0.20 g/cm 3 with about 65 %P.
  • a 600/3 conventional porous ceramic honeycomb substrate of cordierite can have a density of about 0.26 g/cm 3 with about 27 %P
  • the 600/3 low mass porous ceramic honeycomb substrate of cordierite can have a density of about 0.20 g/cm 3 with about 45 %P, a density of about 0.16 g/cm 3 with about 55 %P, or a density of about 0.12 g/cm 3 with porosity of 65%.
  • a 400/6 conventional porous ceramic honeycomb substrate of aluminum titanate composite can have a density of about 0.57 g/cm 3 with about 27 porosity (%P)
  • the 400/6 low mass porous ceramic honeycomb substrate of aluminum titanate composite can have a density of about 0.43 g/cm 3 with about 45 %P, a density of about 0.35 g/cm 3 with about 55 %P, or a density of about 0.28 g/cm 3 with about 65 %P.
  • a 600/3 conventional porous ceramic honeycomb substrate of aluminum titanate composite can have a density of about 0.36 g/cm 3 with about 27 %P
  • the 600/3 low mass porous ceramic honeycomb substrate of aluminum titanate composite can have a density of about 0.27 g/cm 3 with about 45 %P, a density of about 0.22 g/cm 3 with about 55 %P, or a density of about 0.17 g/cm 3 with porosity of 65%.
  • Another approach to reducing the cold start HC release includes providing zeolites to adsorb this large amount of HC.
  • the low mass high porosity substrates provide pores that can accommodate zeolites disposed therein.
  • Zeolites adsorb HC at low temperature and zeolites later release the HC at higher temperature to allow conversion to CO 2 and H 2 O by the warm catalyst.
  • FIG. 3 shows that a substantial amount of HC is adsorbed over the zeolite catalyst.
  • Curve 302 (dashed line) indicates HC before the zeolite adsorber and curve 304 (dot-dashed line) indicates HC after the zeolite adsorber.
  • Curve 306 solid line indicates exhaust temperature before the zeolite adsorber and curve 308 (double solid line) indicates exhaust temperature after the zeolite adsorber.
  • zeolite technology and zeolite coating can be used for diesel oxidation catalysts (DOC) in diesel vehicles.
  • DOC diesel oxidation catalysts
  • the DOC catalysts can have a porosity of less than about 40%, for example, less than about 35%, a porosity of about 10% to about 30%, or even a porosity of about 15% to about 20%.
  • the DOC catalysts can have a median pore size of about 7-10 ⁇ m, and the density of the substrate can be about 0.19-0.35 gm/cm 3 at a 400/4 geometry.
  • the fast light-off, low mass, high porosity substrates can have a porosity of greater than about 40%, for example, greater than about 45%, greater than about 50% and even greater than about 55%.
  • high porosity low mass substrates can have a porosity between about 50% and 70%.
  • the fast light-off high porosity low mass substrate can have a mass of about 190 gm for an about 4 inch (5.1 cm) diameter x about 4 inch (5.1 cm) length, about 600/3 geometry with about 55% porosity.
  • a conventional substrate sample with about 34% porosity has a mass of about 290 gm for about the same size and geometry.
  • FIG. 4 shows schematic cross sections through walls of the conventional substrate having about 34% porosity and the fast light-off high porosity low mass substrate having about 55% porosity.
  • the higher mass, lower porosity wall 402 is represented by a darker shade than the lower mass, higher porosity wall 404.
  • Exemplary embodiments of the disclosure are directed to a porous ceramic body having zeolite disposed in pores of walls of the porous ceramic body and three-way catalyst (TWC) disposed on wall surfaces of the porous ceramic body.
  • this concept includes zeolite coated exclusively inside the pores of the substrate and TWC coated on the wall surfaces of the channels.
  • Zeolite coated inside the pores of the substrate is referred to herein as "in wall” and TWC coated on the wall surfaces is referred to herein as "on wall”.
  • additional zeolite can be coated inside the pores of the substrate, but need not be.
  • FIG. 5 shows schematic cross sections through walls of the conventional substrate 502 having about 34% porosity, the high porosity low mass substrate 504 having about 55% porosity, and the high porosity low mass substrate 504 having zeolite 506 disposed in the pores 508 thereof indicated by a cross hatch fill.
  • the higher mass, lower porosity wall 502 can have a larger median pore size than the lower mass, higher porosity wall 504.
  • the lower mass, higher porosity wall 504 can have a median pore size of about 7 to 10 ⁇ m.
  • TWC 512 is coated on the channel walls 502, 504, and zeolite 506 is disposed in the pores 508 of the lower mass, higher porosity wall 504 illustrated in FIG. 5 insert.
  • "G" represents the gas flow through the channels of the porous ceramic substrate, including, for example, HC, CO, NOx, O 2 , etc.
  • Fast light-off high porosity low mass substrate 504 with zeolite 506 disposed in the pores 508 and TWC 512 disposed on the walls will adsorb HC in the zeolite 506 during cold start of the cycle.
  • the zeolite 506 disposed in the pores 508 can adsorb HC during cold start at and below a certain temperature and desorb HC above the certain temperature, and the TWC 512 disposed on the walls can decompose at least a portion of the desorbed HC in a temperature range having an upper limit above the certain temperature.
  • the certain temperature is a catalyst light-off temperature between about 100°C and about 300°C, for example, a catalyst light-off temperature between about 100°C and about 250°C.
  • zeolite can be in the pores and TWC can be disposed on the walls throughout the entire length of the cell channels of the low mass, high porosity substrate, alternatively zeolite can be disposed only in pores of a portion of the cell channels of the low mass, high porosity substrate.
  • a center portion extending axially and spaced apart from at least one end face may have zeolite disposed in pores of the channel walls.
  • a center portion extending axially and spaced apart from an input end face may have zeolite disposed in pores of the channel walls.
  • the TWC can be disposed on the portion having the zeolite disposed in the pores as well as the portion extending to the at least one end face. Having no zeolite disposed in the channels at an input end portion can provide low mass density allowing the substrate and TWC in such a portion to heat up more rapidly than if zeolite was present in the pores. Having no zeolite disposed in the channels at an outlet end portion can provide, for example, cost savings of catalyst material.
  • zeolite can be disposed only in pores of a first portion of the cell channels of the low mass, high porosity substrate and TWC can be disposed on at least a portion of the walls of the first portion of the cell channels of the low mass, high porosity substrate.
  • the first portion of the walls can extend at least partially from the first end face to the second end face.
  • the first portion of the walls can be spaced apart from the first end face by a first distance, and the first end face can be an inlet side of the porous ceramic honeycomb body.
  • a second portion of the walls can extend from the first end face to the first portion of the walls.
  • the walls extending between the first end face and the first portion of the walls can have a lower density than the first portion of the walls.
  • the first portion of the walls can be spaced apart from the second end face by a second distance.
  • the first distance and the second distance can be substantially the same or different.
  • the first distance and/or the second distance can be about 5% of the length of the low mass, high porosity substrate, for example, about 10%, about 15%, about 20%, about 25%, about 30%, about 40%, or even about 50% of the length of the low mass, high porosity substrate, for example, between about 10 % and 50% of the length of the low mass, high porosity substrate depending on the catalyst light off temperature and HC adsorption capacity.
  • a third portion of the walls extends from the second end face to the first portion of the walls.
  • the second and third portions can have no zeolite disposed inside pores of the walls and have TWC disposed on at least a portion of the second portion and/or the third portion.
  • FIG. 7 illustrates a schematic cross section of a substrate 700 having an input end face 702 and an output end face 704, a first portion 706 of the cell channels having zeolite disposed in the pores of the walls and second and third portions 708, 710 of the cell channels having TWC disposed on the walls, but no zeolite disposed in pores of the walls of the second and/or third portions 708, 710.
  • the first portion 706 having zeolite disposed in the pores of the walls can have TWC disposed on the walls according to these exemplary embodiments of the disclosure.
  • Such an arrangement provides an advantage of keeping the mass density low in the beginning, end or other desired section of the high porosity low mass substrate.
  • the first portion 706, second portion 708, and/or third portion 710 design can be varied as needed to optimize HC adsorption and desorption cycles and manage the desired heat cycles.
  • a high porosity, low mass honeycomb body was coated with zeolite slurry comprising ZSM-5 and AL-20.
  • the zeolite slurry was disposed only in the wall pores.
  • the high porosity, low mass honeycomb body having zeolite disposed in wall was coated with three-way catalyst (TWC) as a layer on the channel wall surfaces.
  • TWC three-way catalyst
  • the sample was fired and tested for hydrocarbon (HC) adsorption and desorption/oxidation using C 3 H 6 in accordance with exemplary embodiments of the disclosure.
  • C 3 H 6 was adsorbed under CS conditions and a significant portion was oxidized during heating cycle (HT).
  • a comparative sample was coated with TWC only and then similarly fired and tested for hydrocarbon (HC) adsorption and desorption/oxidation.
  • the high porosity, low mass honeycomb body substrate having dimensions of about 1 inch (2.54 cm) diameter by about 3 inch (7.62 cm) length was coated with TWC (about 0.1g/cc) using a vacuum coating process, without zeolite.
  • An about 1 inch (2.5 cm) diameter by about 1 inch (2.4 cm) length sample of this comparative catalyzed sample was tested in a light off bench test with about 400 ppm propylene, 5000 ppm carbon monoxide, 500 ppm nitric oxide, 14% CO 2 , 10% steam (H 2 O), 1700 ppm hydrogen (H 2 ), balance nitrogen with space velocity of 90,000 ch/hr (ch refers to volumetric changes so that ch/hr refers to volumetric changes per hour herein) and a total flow of about 17.4 liters/min, using Fourier transform infrared spectroscopy (FTIR) detector.
  • FTIR Fourier transform infrared spectroscopy
  • FIG. 8 shows a raw data plot of propylene concentration (ppm) 802, and catalyst on substrate inlet temperature (°C) 804 and outlet temperature (°C) 806 as function of time (sec) for the sample having on wall TWC.
  • ppm propylene concentration
  • the same high porosity, low mass honeycomb body substrate having dimensions of about 1 inch (2.5 cm) diameter by about 3 inch (7.6 cm) length was coated with ZSM-5 zeolite at about 0.1g/cc loading in the pores followed by coating the same TWC as used in the comparative example at about 0.1g/cc loading on the channel wall surfaces according to exemplary embodiments of the disclosure as described herein.
  • a sample of about 1 inch (2.4 cm) diameter by about 1 inch (2.6 cm) length sample of this exemplary catalyzed sample was tested in a light off bench test with 400 ppm propylene, 5000 ppm carbon monoxide, 500 ppm nitric oxide, 14% CO 2 , H 2 O, 10% steam, 1700 ppm hydrogen, balance nitrogen with space velocity of 90,000 ch/hr and 17.9 liter/min total flow, using Fourier transform infrared spectroscopy (FTIR) detector as explained above for the comparative example.
  • FTIR Fourier transform infrared spectroscopy
  • FIGS. 8 and 9 shows a raw data plot of propylene concentration (ppm) 902, and inlet temperature (°C) 904 and outlet temperature (°C) 910 as a function of time (sec) for the example having on wall TWC and zeolite disposed in wall according to exemplary embodiments of the disclosure.
  • the propylene concentration 902 is much lower at the beginning of the test from about 15 second start time in the exemplary embodiment of the disclosure indicating significant adsorption of propylene in ZSM-5 zeolite coated in the high porosity, low mass honeycomb body substrate pores.
  • the propylene concentration 902 decreases to zero indicating the oxidation reaction over TWC.
  • HC adsorption occurred as indicated by box 906 (See FIG. 10 area between curves 902 and 802).
  • HC desorption and decomposition occurred as indicated by ellipse 908 (See FIG. 10 shaded area between curves 902 and 802).
  • This example exothermic reaction shows the adsorption of propylene (HC) on zeolite and desorption and oxidation during heat up cycle over TWC on the surface.
  • FIG. 10 provides an overlap view of the data from FIGS. 8 and 9 showing the two light-off tests for TWC only in the comparative example and ZSM-5 in pores and TWC on walls in the example of the exemplary embodiment of the disclosure as described herein.
  • the Figure comparing the two examples shows that nearly more than about 60% of the propylene is adsorbed and a small fraction ( ⁇ 10%) of the propylene desorbed and the rest of the hydrocarbon oxidized to CO 2 .
  • These examples clearly demonstrate the advantage of coating zeolite in pores of the fast light-off, high porosity, low mass honeycomb body substrate having TWC coated on wall to provide adsorption at low temperature followed by desorption and oxidation of adsorbed propylene over the TWC at high temperature.
  • Zeolites in automotive catalysts have been found by the applicant to adsorb a broad range of HC, including, for example, from C 3 to C 10 HC chains, alkanes, alkenes, aromatics, and the like.
  • the zeolites have been found to remain stable and reliable for greater than about 100,000 miles (about 161,000 km).
  • Combining the zeolites with the fast light-off, high porosity, low mass honeycomb body substrate deposited in the pores thereof and the TWC deposited on the walls demonstrates the concepts of the exemplary embodiments of the disclosure.
  • the path of the HC to be adsorbed by the zeolite disposed in pores of the walls can be very short leading to rapid adsorption because the walls of the fast light-off, high porosity, low mass honeycomb body substrate are thin.
  • path simply refers to the path the gas takes to penetrate the substrate walls.
  • the path of the desorbed HC to the TWC catalyst is also short for the same reason leading to efficient adsorption at low temperature and desorption and oxidation at high temperature.
  • the TWC disposed on wall tends to heat to catalytic temperature prior to mass in wall.
  • HC desorbed when the bulk of the wall heats up can be readily oxidized by the heated catalyst leading to efficient adsorption at low temperature and desorption and oxidation at high temperature.
  • the thin porous wall heats more easily than a thicker, less porous wall such that the zeolite is efficiently utilized to release adsorbed HC to be oxidized.
  • zeolite in an exemplary embodiment of a diesel oxidation catalyst (DOC) having a lower porosity (%P), for example, in a range from 10%P to 35%P, according to this disclosure, can be disposed in pores in the wall of the DOC and TWC can be disposed on wall as described herein.
  • the zeolite can adsorb HC when the engine cycle runs at a cool temperature followed by desorption and oxidation of HC as described and demonstrated above when the engine cycle runs at a hot temperature.
  • an exhaust system for cleaning a fluid such as engine exhaust can comprise the low mass substrate having high porosity or lower porosity, with zeolite disposed inside pores in wall and TWC disposed on wall of the substrate as described herein.
  • the substrate may be disposed in a housing, which may be deployed in a fluid treatment system such as an exhaust system.
  • the housing may be referred to as a can, and the process of disposing the ceramic honeycomb body in the can may be referred to as canning.
  • FIG. 11 shows exemplary embodiments of exhaust systems including a porous ceramic honeycomb body comprising a zeolite catalyst disposed in pores of the walls and a TWC disposed on surfaces of the walls.
  • the system 3 can include an engine 5 or other source of fluid stream "G", such as exhaust gas stream, to be purified, a housing 7 having a chamber 8 to mount the substrate 9, a filter 11, and an outlet pipe 13, such as a tail pipe or exhaust stack.
  • the housing 7 can have an inlet 12 to direct the gas stream G into the chamber 8 and through the channels of the substrate 9 disposed in the housing chamber 8 whereby the gas stream is purified as described above with regard to some of the exemplary embodiments.
  • the purified gas stream G1 can exit the housing 7 through an outlet 14 and be filtered as it passes through walls of a through-wall filter 11 having inlet and outlet channels sealed with plugs 20 at respective outlet and inlet ends providing a purified and filtered gas stream emission from tail pipe 13.
  • the filter 11 can be a diesel particulate filter or a gas particulate filter and can be upstream or downstream of the substrate 9 according to some of these exemplary embodiments.
  • additional components of the exhaust system may include, for example, a selective catalytic reduction (SCR) catalyst and other compatible components.
  • SCR selective catalytic reduction
  • the substrate is located further from the engine 10 and without a particulate filter 11 such that purified gas stream G1 can directly exit the tail pipe 13. That is, in system 3, the substrate may be close coupled to the engine 5 to provide fast light-off as described above according to various exemplary embodiments of the disclosure. Likewise, while the substrate 9 may not be close-coupled to the engine 10 in the system 21, the system 21 may nevertheless include a filter, SCR catalyst, and the like, and combinations thereof. When the substrate 9 has a low mass density inlet portion as described above with reference to FIG.
  • a sorbing agent to adsorb cold start and/or cold cycle emission constituents and desorb the emission constituents at a temperature near or above a three way catalyst (TWC) light-off temperature and such a TWC to decompose the desorbed emission constituents, according to some of the exemplary embodiments described herein, then the substrate may need not be so closely coupled to the engine, providing more flexibility in system design where space is limited, while still providing full drive cycle emissions below target regulations.
  • TWC three way catalyst
  • components not having the sorbing agent and TWC disposed according to these exemplary embodiments can lead to inefficiencies.
  • a sorbing agent 33 disposed closer to an engine 35 than a TWC 37 would adsorb emission constituents in exhaust gas stream G, but the TWC 37 would be delayed in heating up, even, perhaps, reaching light off temperature after the sorbing agent desorbs the constituents at a desorbing temperature.
  • a TWC 37 closer to the engine 35 would heat up faster, but would not be able to decompose the desorbed constituents.
  • a TWC 37 closer to the engine and an additional TWC 39 further from the engine than the sorbing agent 33 would add additional components and weight and require additional space.
  • the present disclosure relates at least to the following aspects:
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EP3313570B1 (en) 2021-06-02
US20180169634A1 (en) 2018-06-21
EP3313570A1 (en) 2018-05-02
WO2017003981A1 (en) 2017-01-05
JP2018528060A (ja) 2018-09-27
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MX2018000142A (es) 2018-02-19
US20190134614A1 (en) 2019-05-09
CN107810058A (zh) 2018-03-16

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